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Pierre River Mine Project

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HEALTH AENV SIRS 79 – 89<br />

Section 14.1<br />

• the high degree of conservatism incorporated in the consumption patterns of<br />

these residents and the assumed exposure limit.<br />

The RQ values for the cabin and Aboriginal residents were not predicted to<br />

change between the Base Case and Application Case, indicating that all of the<br />

predicted RQ values under the Application Case and PDC are the result of the<br />

Base Case predictions, and that the project is not likely to increase the risk of<br />

long-term exposure to manganese.<br />

Examination of the contributing exposure pathways revealed that consumption of<br />

non-traditional fruits and vegetables represents most (86%) of the predicted RQ<br />

values for the cabin and Aboriginal residents. Lesser contributions were<br />

identified for the ingestion of berries, cattail roots and, in the case of cabin<br />

residents, the ingestion of drinking water. The contribution of each of these<br />

exposure pathways to the RQ values for manganese is shown in<br />

Table AENV 86-6. The contribution from the remaining exposure pathways was<br />

negligible.<br />

Table AENV 86-6: Contribution of Individual Exposure Pathways to Potential Risk<br />

Quotients for Manganese<br />

Contribution<br />

(%)<br />

Exposure Pathway (a) Planned<br />

Base Case Application Case Development Case<br />

ingestion of drinking water (b) Traditional Foods<br />

3 3 3<br />

ingestion of berries 6 6 6<br />

ingestion of cattail roots 2 2 2<br />

Non-Traditional Foods<br />

ingestion of fruit 30 30 30<br />

ingestion of root vegetables 13 13 13<br />

ingestion of leafy vegetables 43 43 43<br />

Note:<br />

(a) The most sensitive life stage was identified as the toddler.<br />

(b) The contribution reported for the ingestion of drinking water is specific to cabin residents. For the Aboriginal<br />

residents, the contribution from the ingestion of drinking water was negligible.<br />

With the exception of the drinking water pathway, all of the contributing<br />

exposure pathways identified above were highly influenced by the measured<br />

background soil concentration of manganese. Regional manganese soil<br />

concentrations ranged from 1.8 to 5,800 mg/kg, with an average concentration of<br />

460 mg/kg. The 95UCLM concentration of 610 mg/kg was used to characterize<br />

background soil concentrations of manganese and subsequently predict<br />

background manganese concentrations in local, natural foods consumed by cabin<br />

and Aboriginal residents.<br />

The assumption that cabin and Aboriginal residents would obtain all (100%) of<br />

their foods (traditional and non-traditional) from local, natural sources, when in<br />

14-30 Shell Canada Limited April 2010<br />

CR029

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